Ocean Accounts

Feasibility Study for Mapping Global Ecosystems

Feixue LI Ph.D Consultant Statistics Division, ESCAP Associate Professor School of Geography and Ocean Science, Nanjing University Email: [email protected]

ESCAP Statistics Division: [email protected]

Table of Contents 1 Introduction ...... 1 2 Overview of the ecosystem classifications ...... 1 2.1 Brief introduction of ecosystem classifications for ...... 1 2.2 Coastal and Marine Ecological Classification Standard (CMECS) ...... 2 2.3 European Union Nature Information System (EUNIS) and Combined Biotope Classification Scheme (CBiCS) ...... 8 2.4 National Intertidal/Subtidal Benthic classification (NISB) ...... 9 2.5 USGS/ESRI Ecological Marine Units ...... 10 3 Data Considerations ...... 12 3.1 Overview ...... 12 3.2 World Ocean Database 2018 and World Ocean Atlas 2013 ...... 13 3.3 Ocean+ Habitat Atlas by UNEP-WCMC ...... 15 3.4 AquaMaps (08/2016) ...... 18 3.5 COPEPOD, the global plankton database ...... 20 3.6 OBIS (Ocean Biographic Information System) ...... 21 3.7 BODC (British Oceanographic Data Centre) ...... 21 3.8 GEBCO (General of the Oceans) ...... 21 3.9 dbSEABED: Information Integration System for Marine Substrates ...... 22 4 Findings and Recommendations ...... 23 4.1 Recommendations on ocean ecosystem classification ...... 23 4.1.1 Recommendations ...... 23 4.1.2 Challenges ...... 24 4.2 Recommendations on global datasets for integration ...... 24 5 Initial Work Plan ...... 26

1 Introduction

The proposed Mapping Global Ocean Ecosystem (MGOE) program aims to produce a series of maps of global coastal and marine ecosystems (e.g. substrate, seagrass, mangrove, coral reef and biotic etc.). The maps will be based on existing spatial datasets and ecosystem classifications of ocean and marine areas.

The ongoing benefits of the Mapping Global Ocean Ecosystem program will facilitate international collaborations for ocean and coastal research, establish a common ocean ecosystem mapping vocabulary and encourage an internationally consistent approach for global ocean ecosystem mapping into the future. We anticipate that the output of this program will facilitate international-scale cross-disciplinary studies of ocean ecosystems. It is our intent that, by collating all the available marine and ocean ecosystem datasets into a single framework, a single classification system and a spatial coordinate, and promoting and extending the availability of these through public use rules, institutions will work collaboratively to address worldwide data gaps and solutions. It is encouraged for researchers worldwide to share their ocean and marine ecosystem data.

Two major tasks are included in this study: reviewing both the existing datasets and the classification frameworks and then summarize recommendations on the best datasets and suitable classification methods for mapping global ocean ecosystems. We have reviewed some of the spatial databases of global ocean. The rules for the database selection focus on open-to-the-public, downloadable and updatability etc. Multiple global datasets are analyzed including the World Ocean Database (WOD), the Ocean+ Habitat Atlas and the AquaMaps etc. Datasets of major ecosystems (e.g. substrate, seagrass, mangrove, coral reef and biotic etc.), and substrate are analyzed and summarized in the following sections. Furthermore, we have reviewed ecosystem classifications for oceans (CMECS, CBiCS, MEOW, GOODS, etc.), in which the Coastal and Marine Ecological Classification Standard (CMECS) is the most systematic and flexible. The framework of CMECS is introduced in the following section in detail.

We have also suggested a work plan and timeline for creating an initial map of global ocean ecosystems, including areas where data are not available. 2 Overview of the ecosystem classifications 2.1 Brief introduction of ecosystem classifications for oceans

In the marine and coastal environment, existing global classification systems remain limited in their spatial resolution. In the absence of compelling global coverage, numerous regional classifications have been created to meet regional needs, such as Coastal and Marine Ecological Classification Standard (CMECS) focusing on United States, Combined Biotope Classification Scheme (CBiCS) focusing on Australia which is based on CEMCS framework, South African National Biodiversity Index, Global Open Oceans and Deep (GOODS) Biogeographic Classification, the National

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Intertidal/Subtidal Benthic classification (NISB) and Marine Ecosystems of the World (MEOW) with definition of 232 marine ecoregions all over the world, etc.

2.2 Coastal and Marine Ecological Classification Standard (CMECS)

The CMEC Standard 1 (https://iocm.noaa.gov/cmecs/) was developed by the US Federal Geographic Data Committee to describe habitat types in Northern America, and is arguably one of the most thorough and well-accepted systems endorsed by the scientific community.

It classifies marine and coastal environments according to two settings – aquatic and biogeographic – and four components – (WC), geoform component (GC), substratum component (SC), and biotic component (BC) (Figure 1). The six elements of the standard represent the different aspects of the seascape, starting with the broadest systems (marine, estuarine, and lacustrine) and narrowing to the most detailed physical and biological features associated with a specific habitat type (biotic community). Descriptive information such as , turbidity, and percent cover are included in CMECS as modifiers. Mapping guidance and protocols, along with dichotomous keys, will be produced to support the implementation of the standard. The Federal Geographic Data Committee (FGDC) has endorsed CMECS as a national standard. Their endorsement followed a long period of public review that included input from a wide variety of stakeholders. As an approved Federal Geographic Data Committee (FGDC) standard, CMECS would be required if federal funds are used for the project.

Figure 1 Relationship between CMECS Settings, Components, Modifiers and Biotopes

1 FGDC (2012). Coastal and Marine Ecological Classification Standard, Federal Geographic Data Committee. 2

The partition of the CMEC Standard into separate hierarchies requires that different ecosystem characteristics are scored and mapped in isolation. This flexibility is advantageous, because it allows the full complexity of ecosystems to be described in fine detail, and each character can be described in the complete absence of knowledge of any others. In contrast to a biotope classification (e.g. EUNIS, CBiCS), this approach is particularly useful in the context of a national scheme where the aims are to both provide a classification framework which can be used into the future to map broad and fine scale community level characteristics, and to accommodate historical data that may often only map one component, e.g. biotic characteristics.

There is also a spatial hierarchy implied by the structure of the scheme, moving from broad descriptions of the Biogeographic and Aquatic Settings, to smaller scale Geomorphology classifications, and to finer descriptions of Substratum Type and the Biotic Community associated with the seafloor. This means that the scheme can be easily tailored to the specific needs of a project and the equipment available for mapping, facilitating its use by a variety of end-users.

CMECS provides two broad-based, complementary settings within which to partition the coastal and marine world (Table 1, Table 2).

The Biogeographic Setting (BS) identifies ecological units based on species aggregations and features influencing the distribution of organisms. Coastal and marine waters are organized into regional hierarchies composed of realms (largest), provinces and ecoregions (smallest).

CMECS adopts the approach described by Spalding et al. (2007) 2 in Marine Ecosystems of the World (MEOW) to characterize Biogeographic Settings occurring in the Estuarine System and in the Marine Nearshore and Marine Offshore Subsystems. MEOW is worldwide in coverage and identifies five realms, eight provinces, and 24 ecoregions in U.S. waters. Representative units include the Gulf of Maine/Bay of Fundy, Carolinian, and Southern California Bight ecoregions.

Biogeographic Settings for the CMECS Oceanic Subsystem are defined in the Global Open Ocean and Deep Seabed (GOODS) Biogeographic Classification (UNESCO 2009). As in MEOW, hierarchies composed of regions, provinces, and ecoregions are identified, but separate suites of terms are applied to benthic and water column habitats.

The Aquatic Settings (AS). CMECS also divides the coastal and marine environment into three Systems: Marine, Estuarine, and Lacustrine. Secondary and tertiary layers of the Aquatic Setting describe Subsystems (e.g., Nearshore, Offshore, and Oceanic within the Marine System) and Tidal Zones within the Estuarine System and Marine Nearshore Subsystem.

2 Spalding, M. D., H. E. Fox, G. R. Allen, N. Davidson, Z. A. Ferdaña, M. Finlayson, B. S. Halpern, M. A. Jorge, A. Lombana, S. A. Lourie, K. D. Martin, E. McManus, J. Molnar, C. A. Recchia and J. Robertson (2007). "Marine ecroegions of the world: A bioregionalization of coastal and shelf areas." BioScience 57(7): 573-583. 3

Table 1 CMECS Settings and Components. AS, BS, BC, and SC are internally hierarchical. WC and GC include non-hierarchical subcomponents

CMECS is organized into four components to record and define the attributes of environmental units and biota within each setting--the Water Column Component (WC), the Geoform Component (GC), the Substrate Component (SC), and the Biotic Component (BC).

The Water Column Component (WC) represents a new approach to the ecological classification of open water settings. The component describes the water column in terms of vertical layering, water and salinity conditions, hydroforms, and biogeochemical features. Modifiers allow users to further subdivide water column units.

The Geoform Component (GC) describes the major geomorphic and structural characteristics of the coast and seafloor. This component is divided into four subcomponents that describe tectonic and physiographic settings and two levels of geoform elements that include geological, biogenic, and anthropogenic geoform features. Representative units include lagoon, ledge, tidal channel/creek, and moraine.

The Substrate Component (SC) describes the composition and size of estuary bottom and seabed materials in all CMECS systems. This component is hierarchical and encompasses substrates of 14 geologic, biogenic, and anthropogenic origin. Particle size classes conform to those developed by Wentworth (1922) and substrate mixes conform to the standard described by Folk (1954). Representative units include sandy mud, coral sand, and construction rubble. See Section 7 for more details.

The Biotic Component (BC) is a hierarchical classification that identifies (a) the composition of floating and suspended biota and (b) the biological composition of coastal and marine benthos. Representative units include Sargassum raft, jellyfish aggregation, Oculina reef, Crassostrea bed, and Rhizophora mangle fringe forest.

CMECS incorporates a list of standard modifiers―a consistent set of characteristics and definitions— as part of each component to describe the nature and extent of observed variability within ecological units. Modifiers allow users to customize the application of the classification in a standardized manner.

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A biotope is defined as the combination of abiotic features and associated species. Users can start with non-living physical characteristics from any of the other CMECS settings or components, if there is no benthic survey. As knowledge of biotopes increases, biotope units and descriptions will be added to CMECS.

CMECS units are spatial tessellations, defined on the basis of attributes observed in specific areas of the seafloor (as viewed from above) or specific segments of the water column (in three-dimensional space).

Table 2 A table of main CMECS components Component Contents

BS

AS

5

WC

GC

6

SC

7

BC

2.3 European Union Nature Information System (EUNIS) and Combined Biotope Classification Scheme (CBiCS)

The EUNIS habitat classification scheme is based on recommendations from Davies and Moss 3 and modifications of the Joint Nature Conservation Committee Classification scheme for Britain and Ireland4. It was developed to describe terrestrial, freshwater, coastal, and marine habitats in the European region only. It differs from the CMEC Standard in its approach in that the marine section classifies biotopes. The biotopes described by the EUNIS scheme are arranged in a single hierarchy, constituting six levels (environment, broad habitat, habitat complex, biotope complex, biotope and sub-biotope) for the marine habitat branch. The upper levels focus on physical characteristics, while the lower levels describe biotic components of the habitat.

The CBiCS (http://www.cbics.org/) is based on both the CMEC Standard and the EUNIS schema, with a total of seven components: biogeographic setting, aquatic setting, water column component, geoform component, substrate component, biotic component and morphospecies component. Each component has a set of hierarchical classes. The first five components (biogeographic setting, aquatic setting, water column component, geoform component, substrate component) are based on CMECS. The sixth component is the biotic component, which is the central component of CBiCS, classifying biological communities that are in a defined habitat. The biotic component was adapted from EUNIS. The last morphospecies component is a completely new

3 Davies, C. E. and D. Moss (2004). EUNIS habitat classification marine habitat types: Revised classification and criterea European Environment Agency European Topic Centre on Nature Protection and Biodiversity. CO249NEW. 4 Connor, D. W., J. H. Allen, N. Golding, K. L. Howell, L. M. Lieberknecht, K. O. Northern and J. B. Reker (2004). The Marine Habitat Classification for Britain and Ireland version 04.05. Joint Nature Conservation Comittee. Peterborough 8 component, provides a scheme for the systematic classification of species and biological groups based on visual characteristics.

The EUNIS and CBiCS are both examples of hierarchical classifications with a shared aim to improve the management and conservation of marine communities. The focus of these schemes is on biotope descriptions – biological communities that consistently occur within a defined set of physical environmental conditions/habitat features. Biotope classifications are advantageous in that they capture the full complexity of biotic communities and how they vary with gradients in environmental conditions, e.g. exposure, salinity, light. They also allow for classes to be described as much by dominant taxa as by frequently occurring but less abundant or rare species, which can be an important consideration for conservation and management of marine environments.

However, the combination of both physical and biological attributes into a single hierarchy in this structure means that it is impossible to reclassify existing data, which often only maps a single habitat characteristic, e.g. biota. Source units get ‘stuck’ at the higher levels of the hierarchy, resulting in reclassified units with concepts much broader than the original source concept. Furthermore, the ecological meaning of biotope descriptions is not often intuitive, and labels are typically long and complicated, e.g. sublittoral mud in variable salinity (estuaries) (EUNIS). To avoid this implicit loss of information, the Seamap Australia scheme, in which CMECS is adopted, has not adopted a biotope approach to the classification of benthic marine habitats.

Figure 2 Six levels of the biotic component of the EUNIS habitat classification scheme

2.4 National Intertidal/Subtidal Benthic classification (NISB)

The National Intertidal Subtidal Benthic (NISB) Classification Scheme developed by Mount and Bricher 5 in 2008 defines broad habitat types in Australia in terms of substratum type (e.g. boulder, rock) and structural biota (e.g. seagrass, coral) with the

5 Mount, R. and P. Bricher (2008). Estuarine, Coastal and Marine National Habitat Map Series user guide First PAss Coastal Vulnerabiliy Assessment. Australian Government Department of Climate Change, National Land and Water Resources Audit, University of Tasmania, Hobart 9 option of including a range of environmental attributes (e.g. depth, light availability, exposure) as additional descriptors. The classification range extends from the Highest Astronomical (HAT) to the outer edge of the (~200 m depth).

The use of broad habitat types in the NISB scheme makes for clear and intuitive habitat classes. However, a limitation of this scheme is that the classes are not defined at a finer resolution. Many habitat mapping initiatives include data to species level, and the option to include classification at this level is necessary. Furthermore, while the NISB scheme captures the dominant habitat types, many commonly occurring and/or important habitat types are not described within the framework (e.g. rhodolith beds). This leads to an inability to adequately describe the diversity of marine ecosystems.

The classification scheme was designed to be compatible with other schemes employed by mapping groups in Australia, however, it was structured as an attribute- based system and so was not hierarchical. It could therefore not account for the nested scales of different mapping initiatives and this may explain why it was not readily adopted by the Australian seabed mapping community.

2.5 USGS/ESRI Ecological Marine Units

Ecological Marine Units (EMUs)6are baseline 3D mapped ecosystems of the ocean that have been classified through statistical clustering. EMUs come from an unprecedented 3D point mesh framework of 52 million global measurements of 6 key ocean variables over a 50-year period at a horizontal resolution of 1/4˚ by 1/4˚, over 102 depth zones. The deterministic parameters are temperature, salinity, dissolved oxygen, nitrate, phosphate, and silicate.

The data used in constructing the EMUs comes from World Ocean Atlas (WOA), which is a compendium of data from a variety of ocean research and monitoring programs over the past five decades. The complete set of variables from the 2013 WOA is used and it contains over 52 million points (ocean mesh).

Temporally, the WOA archive is available in seasonal, annual, and decadal resolutions. Spatially the WOA has a horizontal spatial resolution of 1/4˚ × 1/4˚ for temperature and salinity, and 1˚ × 1˚ for oxygen, nitrate, phosphate, and silicate. Resolution 1˚ × 1˚ were downscaled to the 1/4˚ resolution to reconcile all data to a common working horizontal resolution. In the vertical dimension, points are located at variable depth intervals, ranging from 5 m increments near the surface to 100 m increments at depth. A total of 102 depth zones extend to 5500 m.

The procedure for defining an EMU are as follows: Firstly, constructing an “empty” ocean point mesh using the 52,487,233 WOA point locations, and then constructing the water column by attaching the WOA attribute data to those points. Secondly,

6 Sayre, R.G., D.J. Wright, S.P. Breyer, K.A. Butler, K. Van Graafeiland, M.J. Costello, P.T. Harris, K.L. Goodin, J.M. Guinotte, Z. Basher, M.T. Kavanaugh, P.N. Halpin, M.E. Monaco, N. Cressie, P. Aniello, C.E. Frye, and D. Stephens (2017). A three- dimensional mapping of the ocean based on environmental data. 30(1): 90-103. 10 statistically clustering the points in the mesh in order to identify environmentally distinct regions in the water column. The clustering was blind to both the depth of the point and the thickness of the depth interval at that point’s vertical position in the water column. The clustering was implemented using SAS (Statistical Analysis System) software, the optimum cluster number 37 was determined by inspection of the behavior of the pseudo F-statistic. Finally, the clusters were labeled using the naming criteria of the CMECS. The labels begin with depth zone assignments, followed by a concatenation of the CMECS descriptors for temperature, salinity, and dissolved oxygen.

Global ocean is divided into 37 EMUs in 3D space. Twenty-two of the EMUs are large, with essentially global or large regional distributions, while the 15 others are small, shallow, and coastal, and collectively represent only about 1% of the ocean volume. The distribution of EMUs is shown in the figure3 and figure4.

Figure 3 Vertical distribution of the 37 EMUs

EMU may be used to map the global ocean ecosystem in a 3D form. The biggest challenge in marine mapping is that the ocean is a three-dimensional space, different species distribute in different depths. The “land cover map for the ocean” can’t express all kinds of ocean data very well. The proposal of EMU provides a new way of ocean three-dimensional mapping. EMUs embody open, accessible data and serve as the basis for a variety of marine spatial research such as ocean conservation and resource management.

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Figure 4 Global distribution of one EMU (named Bathypelagic, Very Cold, Euhaline, Severely Hypoxic, High Nitrate, Medium Phosphate, High Silicate)

Disclaimer: The designations employed and the presentation of material on this map do not imply the expression of any opinion whatsoever on the part of the Secretariat of the United Nations concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries.

However, limitations in EMUs are related to both temporal scaling dimensions and parameters selected for the clustering. First, the 57-year mean values for the six parameters were used to map EMU, and it prohibits the assessment of temporal variability and trends. Second, the clustering of oceanic data to derive EMUs was based on the six variables in the WOA data set. The addition of other variables would likely influence the oceanic partitioning. The inclusion of data on particulate organic carbon (POC), carbonate contents, and patterns might influence the clustering results. Furthermore, while calling these 37 volumetric regions EMUs, we can find that their true ecological character has not yet been established. 3 Data Considerations 3.1 Overview

As we know, there are some specialized maps for individual ecosystem types (coral, mangrove, seagrass, etc.), bathymetry, , species ranges, etc. There are also several comprehensive maps for continental ocean regions, countries and sub-national areas. Our aim is to create a comprehensive map for the global ocean ecosystem, that is, coastal and marine areas. For mapping global ocean ecosystem, it is a necessity to create a collection of standardized spatial ocean data with regular production, quality control and update mechanisms.

We have reviewed some of existing global ocean ecosystem datasets in accordance with a general ocean ecosystem classification framework. Some of the datasets are introduced in the following section.

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3.2 World Ocean Database 2018 and World Ocean Atlas 2013

The World Ocean Database (WOD) (https://www.nodc.noaa.gov/OC5/WOD/pr wod.html) is a collection of scientifically quality-controlled ocean profile and plankton data that includes measurements of temperature, salinity, oxygen, phosphate, nitrate, silicate, chlorophyll, alkalinity, pH, pCO2, TCO2, Tritium, Δ13Carbon, Δ14Carbon, Δ18Oxygen, Freon, Helium, Δ3Helium, Neon, and plankton.

WOD incorporates 20,547 different datasets received and archived at NCEI (National Center of Environment Information). The data represent the results of 216,845 oceanographic cruises on 8,215 different platforms from 798 institutes around the world and 553 separate projects.

There are 3.56 billion individual profile measurements (depth/pressure vs. measured variable) in the WOD. Of these 1.95 billion are temperature, 1.13 billion salinity, 260 million oxygen, and 4.5 million plankton measurements. There are an additional 22 million meteorological/ state observations. These measurements make up the 15.7 million oceanographic casts in the WOD.

The WOD data are available online presorted by 10° geographic squares, by year, or user-specified via WOD select data selection tool at standard or observed depth levels. All the WOD ASCII output files are in GZIP compressed format as “.gz” files and can be uncompressed to “.csv” files. The data of WOD shows as the formats of excel csv or grid, which can be analyzed and visualized in GIS platforms. All data are downloadable from the WOD website (https://www.nodc.noaa.gov/OC5/WOD/ readwod.html) or ftp (ftp.nodc.noaa.gov )

Table 3 The main sub-datasets in WOD Dataset Content Bottle, low resolution CTD (Conductivity, Temperature and Depth), and OSD plankton data MBT Mechanical Bathythermograph data XBT Expendable Bathythermograph data CTD High resolution CTD data APB Autonomous Pinniped Bathythermograph data DRB Drifting Buoy data MRB Moored Buoy data PFL Profiling Float data UOR Undulating Oceanographic Recorder data GLD Glider data

WOA13 (https://odv.awi.de/en/data/ocean/world-ocean-atlas-2013/) is an atlas describing climatological mean fields on both a quarter- and on a one-degree longitude/latitude grids. It is provided by the U.S. National Oceanographic Data Center (NODC). Statistical fields used in quality control (but not objectively analyzed climatological means) are available on a five-degree longitude/latitude grid.

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The data files in WOA13 are available in four formats: Climate and Forecast (CF) compliant netCDF, comma-separated value (csv) format, ArcGIS-compatible shapefiles, and compact grid format (a legacy WOA ASCII format). The periods are annual, seasonal (by three-month periods; Winter = January, February, and March; Spring, Summer, and Fall are the sequentially following three-month periods), and monthly. Time spans are mostly decadal (10 years) spans.

The online version of World Ocean Atlas 2013 Figures V2 (WOA013FV2) contains a collection of "JPEG" images of objectively analyzed fields and statistics generated from the World Ocean Atlas 2013 V2. The images of the features in 33 depth levels can be viewed on the website of WOA13.

Table 4 The images in World Ocean Atlas 2013 V2 Temperature (°C) Salinity (unitless) Density (kg/m3) beta version Conductivity (S/m) Dissolved Oxygen (ml/l) Percent Oxygen Saturation (%) Apparent Oxygen Utilization (ml/l) Silicate (µmol/l) Phosphate (µmol/l) Nitrate (µmol/l) Figure 5 Sample map of WOA

Disclaimer: The designations employed and the presentation of material on this map do not imply the expression of any opinion whatsoever on the part of the Secretariat of the United Nations concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries.

Each individual data value and each profile in WOD18 has quality control flags associated with it. A description of these flags and general documentation describing 14 the software for reading and using the WOD18 database are found in Garcia et al. (2018)7. WOD also includes quality control flags assigned by data submitters. It is clear that there are both Type I and Type II statistical errors (for normal distributions) associated with these flags. There are some data that have been flagged as being questionable or unrepresentative when in fact they are not. There are some data that have been flagged as being “acceptable” based on our tests, which in fact may not be the case. In addition, the scarcity of data, non-normal frequency distributions, and the presence of different water masses in close proximity result in the incorrect assignment of flags. Oguma et al. (2003; 2004)8 discuss the skewness of oceanographic data. The WOD flags represent data values used or not used in the calculation of the WOA climatological mean fields.

3.3 Ocean+ Habitat Atlas by UNEP-WCMC

The Ocean+ Habitat Atlas was originally curated by UNEP-WCMC (United Nations Environment World Conservation Monitoring Centre) (http://data.unep-wcmc.org/) in collaboration with hundreds of data contributors, ranging from governments to individual researchers. The aim of Ocean+ Habitat Atlas is to produce the first online, authoritative database on the known extent of ecologically-important ocean habitats, such as seagrasses, warm- and cold-water corals, mangroves and salt marshes, and to update this database consistently over time.

As of January 2018, the atlas consists of several datasets that include global distribution of seagrasses, warm- and cold-water corals, mangroves and saltmarshes (Figure 6).

Data types: raster or 1-2 shapefiles, one with polygons and one with points, and both including associated spatial and tabular information on key attributes; one source table identifying the sources of the data (provider, date and metadata etc.).

The data are also available for download from the Ocean Data Viewer in file geodatabase, KML, ESRI Web Map Service (WMS) and CSV formats. The atlas is based on the Geographic Coordinate System: World Geodetic Survey (WGS) 1984.

Data update: the data providers are required to update country-level data at least every five years.

The Atlas will only store one version of a given habitat and all records should be verified by an authoritative source. The ‘Verification’ (VERIF) field allows two values: Government Verified and Expert Verified.

Quality assurance: three indicators are calculated for every release, which will be reviewed at each release: percentage of records with boundaries in polygon format (where relevant), percentage of data attributes reported, and percentage of records

7 Garcia, H. A., C. Y. Rodriguez, R. Silva, E. Mendoza, and L. A. Vega (2018). Determination of the potential thermal gradient for the mexican pacific ocean. Journal of Marine Science and Engineering, 6(1): 20.

8 Oguma, S., and Y. .Nagata (2002). Skewed water temperature occurrence frequency in the sea off sanriku, japan, and intrusion of the pure kuroshio water. Journal of Oceanography, 58(6): 787-796. 15 updated, or confirmed without change, by the data provider in the last 5 years.

Table 5 Dataset description for Ocean+ Habitat Atlas by UNEP-WCMC

Public Dataset Sub-dataset Geometry type Timespan Data type ation date Global Distribution of Coral Empirical Polygon, point 1954-2018 2018 Reefs observation Global Distribution of Coral Polygon, point, 1915-2014 2018 Reefs (cold water) other Global Distribution of Coral Coral reefs Polygon, point Reefs (warm water) Reefs at Risk Revisited Polygon 2011-2011 Modelled data 2011 Global Distributions of Habitat Suitability for Cold-Water 2012-2012 Modelled data 2012 Octocorals Global Mangrove Watch Polygon 1996-2016 2018 Global Distribution of Polygon 2014-2014 Modelled data 2018 Modelled Mangrove Biomass Mangrove Empirical World Atlas of Mangroves Polygon 1999-2003 2010 observation Global Distribution of Empirical Polygon 1997-2000 2011 Mangroves USGS observation Global Distribution of Empirical Polygon, point 1934-2015 2017 Seagrasses observation Global Seagrass Species Polygon Metric Seagrass Richness A Modelled Global Distribution of the Seagrass Polygon Modelled data Biome Global distribution of Empirical Saltmarsh Polygon, point 1973-2015 2017 Saltmarshes observation Mean Sea Surface Raster 2003-2007 Modelled data 2008 Productivity in June Mean Sea Surface Raster 2003-2007 Modelled data 2008 Sea Productivity in December surface Mean Annual Sea Surface Raster 2009-2013 2015 Chlorophyll-a Concentration Mean Annual Sea Surface Empirical Raster 2003-2007 2008 Temperature observation Sea Global Distribution of Sperm Raster 2013-2013 Modelled data 2013 animals Whales

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Public Dataset Sub-dataset Geometry type Timespan Data type ation date Global Distribution of Sei Point 2013-2013 Modelled data 2013 Whales Global Distribution of Point 2013-2013 Modelled data 2013 Bowhead Whales Global Distribution of Point 2013-2013 Modelled data 2013 Northern Bottlenose Whales Global Distribution of Atlantic Point 2013-2013 Modelled data 2013 Spotted Dolphins Global Distribution of Melon- Point 2013-2013 Modelled data 2013 Headed Whales Global Distribution of Hector's Point 2013-2013 Modelled data 2013 Dolphins Global Distribution of Grey Point 2013-2013 Modelled data 2013 Seals Global Distribution of Point 2013-2013 Modelled data 2013 Hawaiian Monk Seals Global Distribution of Point 2013-2013 Modelled data 2013 Northern Fur Seals Global Distribution of Sea Empirical polygon 1993-1993 1999 Turtle Feeding Sites observation Global Distribution of Sea Empirical other 1949-1993 1999 Turtle Nesting Sites observation Global Distribution of Polygon, point 2011-2011 Modelled data 2011 and Knolls Empirical Global Estuary Database polygon 2003-2003 2003 observation Global Patterns of Marine polygon 1900-2009 Metric 2010 Biodiversity Global Distribution of Dive Empirical Point 2001 Centres observation Global Critical Habitat Others Screening Layer (Published) Raster 2017-2017 Classification 2017 (Area of biodiversity importance) Marine Ecoregions and Pelagic Provinces of the polygon 2007-2012 Classification 2015 World (2007, 2012) World Database on Protected Areas(Area of biodiversity Polygon, point 2016 importance)

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Figure 6 Mapping major ecosystem datasets of Ocean+ Habitat Atlas

Disclaimer: The designations employed and the presentation of material on this map do not imply the expression of any opinion whatsoever on the part of the Secretariat of the United Nations concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries 3.4 AquaMaps (08/2016)

AquaMaps (https://www.aquamaps.org/) is a joint project of FishBase and SealifeBase. AquaMaps includes standardized distribution maps for over 25,000 species of fishes, marine mammals and invertebrates. These estimates of species preferences, called environmental envelopes, are derived from large sets of occurrence data available from online collection databases such as GBIF (Global Biodiversity Information Facility, www.gbif.org ) and OBIS (Ocean Biogeographic Information System, www.obis.org ), and from independent knowledge from the literature about the distribution of a given species and its habitat usage that are available in FishBase (and in SeaLifeBase and AlgaeBase for non-fish).

Six major environmental parameters are included in the dataset: depth, temperature, salinity, , sea ice concentration and distance to land.

Depth: refers to the minimum and maximum cell bathymetry derived from ETOPO 2min negative bathymetry elevation; in meters.

Temperature:

 Observed mean annual surface and bottom sea temperature derived from NCEP SST (1982-1999); in degrees Celsius.  Modeled current mean annual surface and bottom sea temperature from the IPSL Climate model SRES A2 (2001-2010); in degrees Celsius.  Modeled 2100 mean annual surface and bottom sea temperature from the IPSL Climate model SRES A2 (2090-2099); in degrees Celsius.

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Salinity:

 Observed mean annual surface salinity provided by the World Ocean Atlas (1982-1999); in PSU.  Observed mean annual bottom salinity provided by the World Ocean Atlas Bottom Source Information (1990-1999); in PSU.  Modeled current mean annual surface and bottom salinity from the IPSL Climate model SRES A2 (2001-2010); in PSU.  Modeled year 2100 mean annual surface and bottom salinity from the IPSL Climate model SRES A2 (2090-2099); in PSU.

Primary Production:

 Proportion of annual primary production in a cell from http://seaaroundus.org /PrimaryProduction/Interpolation_method.htm ; in mgC·m-²·day -1.  Modeled proportion of annual primary production in a cell from the IPSL Climate model SRES A2 (2001-2010); in mgC·m-²·day -1.  Modeled year 2100 proportion of annual primary production in a cell from the IPSL Climate model SRES A2 (2090-2099); in mgC·m-²·day -1.

Sea Ice Concentration:

 Observed mean annual ice cover as derived from the National Snow and Ice Data Centre (1979-2002), http://nsidc.org/data/nsidc-0051.html ; in percent.  Modeled current mean annual ice cover from the IPSL Climate model SRES A2 (2001-2010); in percent.  Modeled year 2100 mean annual ice cover from the IPSL Climate model SRES A2 (2090-2099); in percent.

AquaMaps predictions of species distributions are generated in a two-step process. In the first step, maps are computer-generated using algorithm-derived input parameter settings based on occurrence data filtered with information on the distribution and habitat usage of a species (e.g., depth range, geographic range limits, environment occupied according to adult feeding or breeding behavior). In the second step, experts can review, edit and approve the computer-generated AquaMaps: Algorithm and Data Sources for Aquatic Organisms 2 maps. These expert-reviewed maps can, from then on, only be updated by experts. The computer-generated maps are updated every 1- 2 years.

Both observed and modelled data are used in AquaMaps. All data can be downloaded as .csv files.

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Figure 7 Marine AquaMaps Statistics

3.5 COPEPOD, the global plankton database

COPEPOD’s global plankton database component (https://www.st.nmfs.noaa.gov /plankton/about/databases.html) provides an integrated data set of quality-reviewed, globally distributed plankton abundance, biomass and composition data. COPEPOD works closely with NOAA programs (e.g., the Fisheries And The Environment (FATE) and Integrated Ecosystem Assessment (IEA) programs) and a variety of international scientific organizations.

Three levels of data can be found in the database: (1) Raw Data Compilation, with many different methods and units; (2) Standardized Spatial Field, in-situ fields without interpolation or modelling, without missing-data or gap-filling; (3) Analyzed Spatial Field, modelled or interpolated gap filling.

All the data can be downloaded as “.csv” files with longitude and latitude coordinates, and they can be converted to Esri shapefiles. COPEPOD first went online in August of 2004. Full database content and method summaries are released roughly every few years (e.g. COPEPOD-2014, COPEPOD-2010, COPEPOD-2007, COPEPOD-2005), with new data content added each month.

Figure 8 Example of Zooplankton data from COPEPOD

Disclaimer: The designations employed and the presentation of material on this map do not imply the expression of any opinion whatsoever on the part of the Secretariat of the United Nations concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries

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The Time Series Metabase is an information (i.e., "metadata") database providing details and graphical results from over 350 marine ecological time series. The Metabase contains investigator and project contact information, sampling and methods details, and a collection of standardized summary graphics for each time program.

3.6 OBIS (Ocean Biographic Information System)

OBIS (https://www.obis.org/) emanates from the Census of Marine Life (2000-2010) and was adopted as a project under IOC-UNESCO’s International Oceanographic Data and Information (IODE) programme in 2009. More than 20 OBIS nodes around the world connect 500 institutions from 56 countries. Collectively, they have provided over 45 million observations of nearly 120 000 marine species, from Bacteria to Whales, from the surface to 10 900 meters depth, and from the Tropics to the Poles. The datasets are integrated so you can search and map them all seamlessly by species name, higher taxonomic level, geographic area, depth, time and environmental parameters.

3.7 BODC (British Oceanographic Data Centre)

As part of the UK’s National Oceanography Centre, British Oceanographic Data Centre (BODC) provides instant access to over 130,000 unique data sets (https://www.bodc.ac.uk/data/bodc_database/nodb/search/). It provides International , Historical BPR (bottom pressure recorder data) data, floats, GEBCO’s (see below) gridded bathymetric data, AMT CTD and underway, UK Network and Historical UK tide gauge data.

GEBCO’s gridded bathymetric data sets are global terrain models for ocean and land. They are maintained and distributed by BODC on behalf of GEBCO. The GEBCO_2019 Grid is GEBCO’s latest global terrain model at 15 arc-second intervals. The Grid is available to download as a global file in netCDF format, or for user-defined areas in netCDF, Esri ASCII raster or GeoTiff formats. (https:// www.bodc.ac.uk/data/hosted_data_systems/gebco_gridded_bathymetry_data/ )

3.8 GEBCO (General Bathymetric Chart of the Oceans)

GEBCO (General Bathymetric Chart of the Oceans) (https://www.gebco.net/) produces and makes available a range of bathymetric data sets and products. The dataset includes global gridded bathymetric data sets; the GEBCO Gazetteer of Undersea Feature Names; the GEBCO world map.

The gazetteer is available to view and download via a web map application, hosted by the International Hydrographic Organization Data Centre for Digital Bathymetry (IHO DCDB) co-located with the US National Centers for Environmental Information (NCEI). The data are available in a number of formats including spreadsheets, shapefile, KML, WMS and ArcGIS layer and can be accessed as a REST-style API.

Seabed 2030 is a collaborative project between the Nippon Foundation and GEBCO. It aims to bring together all available bathymetric data to produce the definitive map of the world ocean floor by 2030 and make it available to all. 21

3.9 dbSEABED: Information Integration System for Marine Substrates dbSEABED (https://instaar.colorado.edu/~jenkinsc/dbseabed/) creates unified, detailed mappings of the materials that make the seafloor by efficiently integrating thousands of individual datasets. The goal is to bring decades of seabed information - and today's information - from , biology, engineering and surveys into one seabed mapping that can fulfill the community needs for ocean-bottom information on many spatial scales. The system deals with seabed texture, composition, acoustic properties, colour, geology and biology.

Figure 9 Point data distribution in dbSEABED 2015

Disclaimer: The designations employed and the presentation of material on this map do not imply the expression of any opinion whatsoever on the part of the Secretariat of the United Nations concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries

Huge data entry efficiencies come from programs that prepare the data for use in standard databases. As evidence of its efficiency, the US, Australian and global coverages together hold integrated data for over 3,000 datasets and 5 million described seafloor sites.

The scale of operation is local, national and global: shorelines, bays, seaways, national EEZ's, ocean basins, and worldwide. The database deals with coastal, estuarine, inshore, continental shelf, continental slope and very deep-sea environments. dbSEABED is point-data based, so spatial resolution improves as more datasets are added. Gridded and vector mappings of the seafloor materials are computed from the point-data coverages. Accuracies are the same as for the original survey data; system precision is 1m; datum is WGS84.

The data is presented in the organization of a multidimensional cube, one dimension per parameter. Every parameter, not just the spatial data, can then be a dimension for query, retrieval, plotting. The hypercube structure has other benefits. It is not software-

22 specific and can be imported into many analysis packages including Matlab, ArcGIS, ArcView, MS Access, GMT, OceanDataView. Access to the complete data is full and direct through the hypercube, or per-core through KML Google .

Quality assurance is achieved by checks on data at data entry, by error-trapping in the data-processing software, and by working the data intensively in various collaborative research programs. dbSEABED was devised to be robust in an inexact and incomplete information environment - marine geosciences. An uncertainty budget is calculated with map outputs. 4 Findings and Recommendations

In summary, mapping global ocean ecosystem is feasible concerning the ocean ecosystem classification and data availability. For the classification system, CMECS is recommended to map global ocean ecosystem. For the datasets, coupling multiple datasets is practicable in creating the map. However, it is a very complicated and tough task partly due to the fluidity of most of the components in ocean ecosystem.

4.1 Recommendations on ocean ecosystem classification 4.1.1 Recommendations

CMECS is recommended to map global ocean ecosystem. CMECS is applicable to mapping global ocean ecosystem given that CMECS provides a means for classifying ecological units using a simple, standard format and common terminology. It has the following advantages.

(1) CMECS is compatible with relevant standards and based on most recent publications. CMECS is compatible with relevant U.S. FGDC-endorsed national standards. This compatibility is intended to facilitate studies across the transition between terrestrial and coastal aquatic ecosystems. Furthermore, CMECS draws from some of the most recent publications and studies. The three hierarchical categories of the Biogeographic Setting (BS) are based on the Marine Ecoregions of the World (MEOW) technique (Spalding et al., 2007). Water column and benthic environments are addressed in the classification. The principles guiding the MEOW approach were applied to oceanic benthic and water column settings and published as the Global Open Oceans and Deep Seabed Biogeographic Classification (GOODS) by scientists working under the aegis of UNESCO (United Nations Educational, Scientific and Cultural Organization) (UNESCO 2009).

(2) CMECS has a systematic and flexible framework composed of four components, two settings and multiple modifiers, which cover most of the water conditions, seafloor condition and biotic status. Furthermore, both the Biogeographic and Aquatic Settings and components can be extended according to the application areas.

(3) CMECS shows data-friendly features. CMECS allows investigators to determine the types of data to be collected. Its structure accommodates data from multiple disciplines at multiple spatial and temporal scales, and its use is not limited to 23

specific gear types or to observations made at specific spatial or temporal resolutions. Traditionally, spatial data have been organized and represented in four general formats: points, lines, polygons, and grids. Although CMECS has been focused on biological communities, CMECS units are very amenable to each of the major spatial data types.

(4) CMECS has been applied successfully in both U.S. coastal study and Australia after extension on the original structure. These application cases have approved CMECS’s validity and extensibility.

4.1.2 Challenges

(1) Dynamic water column and biotic components at multiple temporal scales ranging from daytime to nighttime, month, and climate change etc. CMECS recognizes that the seafloor and water column are dynamic. A given area of seafloor may be characterized differently over time. Users of CMECS are encouraged to identify all CMECS units present during an observation—regardless of their likely longevity. Any CMECS observation should be considered a “snapshot in time,” in order to provide the most information.

(2) It is hard for collecting data at multiple time points or periods. It is hard for collecting data at one-time point or period given that very few or no fixed water columns maintain over time due to the fluidity of water, an ever-present transfer between ocean surface and atmosphere, etc.

(3) More application tests should be carried out and the results needing an assessment before global mapping. The application tests should be implemented both in coastal regions all around the world and at multiple scales with progressive details requirements. The necessary extensions should be clarified before global use.

4.2 Recommendations on global datasets for integration

On the one aspect, in most cases, one feature of ocean conditions (such as temperature, depth, etc.) is contained in multiple datasets. On the other aspect, an ocean dataset covers limited ecosystem components. Coupling multiple datasets are practicable in creating a global ocean ecosystem map.

(1) For data describing the water column, WOA is recommended as a reference. WOA is a relatively comprehensive global ocean dataset which is composed of multi formats: points, lines, polygons, and grids. Both observed data and modelled data are included in the datasets, both of which have passed quality control by the government or the experts. The data of multi-points in time can be downloaded from its website. The data contents focus on biochemical features of the ocean conditions that can be used with other databases, such as Ocean+ by UNEP- WCMC covering major ocean and coastal ecosystem distributions and conditions.

(2) For data related to the global ocean ecosystem, Ocean+ by UNEP-WCMC can be used. Ocean+ Habitat Atlas is to produce the first online, authoritative database on 24

the known extent of ecologically-important ocean habitats, such as seagrasses, warm- and cold-water corals, mangroves and salt marshes, and to update this database consistently over time.

(3) For data describing the geoform, GSHHG (Global Self-consistent, Hierarchical, High- resolution Geography Database) is recommended as a reference. GSHHG can provide data for mapping Beach, Beach Berm, Boulder Field, Bank, Shore and Shelf.

(4) For mapping the biotic, CMECS divided the biotic into Planktonic Biota Benthic/Attached Biota. The COPEPOD’s global plankton database component and WOD Ocean Station Data (OSD) can provide Plankton data. NOAA’s Coral Research and Technology Program (DSCRTP) CoRIS: Coral Reef Information System can provide reef biota data.

(5) For data describing the substrate, the dbSEABED, Information Integration System for Marine Substrates are suggested. dbSEABED is based on point data. This database includes seabed texture, composition, acoustic properties, color, geology and biology.

The distributions of many marine species (such as fish and plankton) are dynamic in space and time, and some movements made by individuals are regularly, while others are erratic. Mapping such mobile species is challenging. To solve this problem, we can use the relative probability of occurrence to show the range of the species. For example, the AquaMaps is a tool for generating model-based, large-scale predictions of natural occurrences of mobile species. The AquaMaps provides standardized range maps for marine species using available information on species occurrence.

The Ocean+ Habitat Atlas included some species range datasets, an example of global distribution of Sei Whales is shown in Figure 10. The dataset contains continuous probabilities of occurrence of Sei Whale as a global grid of 0.5° resolution.

Mapping marine conditions require a lot of data, which comes from different websites. Some of the recommended datasets can be found in Table 5. Furthermore, NOAA National Centers for Environmental Information provides lots of regional datasets, which can be used after a detailed review.

Table 6 shows an initial idea on linking CMECS and available global ocean ecosystem data, more detail should be discussed when creating a draft map. Table 7 shows the list for available datasets reviewed for mapping global ocean ecosystem.

An example of a global coral reef distribution map using CMECS and coral reef data from NCEI (https://www.ncei.noaa.gov/maps/deep-sea-corals/mapSites.htm) is shown in Figure 11.

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Figure 10 Examples of expression methods for mobile species

Disclaimer: The designations employed and the presentation of material on this map do not imply the expression of any opinion whatsoever on the part of the Secretariat of the United Nations concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries

Figure 11 Example of global coral reef distribution using CMECS

Disclaimer: The designations employed and the presentation of material on this map do not imply the expression of any opinion whatsoever on the part of the Secretariat of the United Nations concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries 5 Initial Work Plan

(1) It is a must to determine the spatial and temporal scale and granularity when creating a draft map for the global ocean ecosystem. Thus, the primary issues should

26 be addressed, including minimum mapping unit, CMECS units used and date/time and duration of the study (to address temporal issues), etc. To some extent, it is determined by datasets. In turn, it will give requirements and guidance for datasets selection and coupling. This may need 1 person-month.

(2) Then, the potentially available datasets should be analyzed in detail and then some datasets at a certain spatial scale and time point are adopted. Ancillary data used to support the analysis also need to be determined (e.g. a bathymetric grid used to determine tidal zones). In this process, the example data need to be downloaded to clarify the quality of these data. This may take 1 person-month.

(3) Due to the gaps in the data format, spatial and temporal resolutions of various datasets, some preprocessing steps are needed to unify the datasets so that they can be combined to map land cover for the global ocean. Preprocessing steps include but not limited to format conversion, projection conversion, data correction and validation. It may take 1 person-month.

(4) To define a crosswalk from an existing system into CMECS is the best way to preserve the original data information and also support standard mapping, once the datasets are determined. It is important to note that successful crosswalking is dependent on an understanding of the parameters behind the original data development and equivalency between classification systems—not only at the unit definition level, but also in hierarchical context. 2 person-months are suggested.

(5) The last process should be linking CMECS and data at needed spatial and temporal scale. CMECS can organize data of different levels and scales. Using CMECS to classify all kinds of data, for integrated mapping. It may take 1 person- month.

Totally, six person-months are suggested for creating an initial test map. Furthermore, workshops on CMECS training and major datasets introduction are essential for research team to achieve the goal of mapping global ocean ecosystem. And Pilot studies of the application of CMECS and the existing data for mapping typical regional ocean ecosystem are encouraged. For the workshop on CMECS training, researchers of CMECS development and application, experts in the field of the ocean ecosystem and ocean science should be invited. For the workshop on major ocean ecosystem data requirement and provision discussion, researchers from ocean science, ocean ecosystem data providers and managers in coastal regions (e.g. Asian Pacific, EU, etc.) are needed.

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Table 6 A table of major CMECS components and suitable datasets

CMECS Setting/Comp Class Subclass Datasets Datasets description onent Arctic Temperate Northern Atlantic BS Temperate Northern Biogeographic Pacific Setting Tropical Atlantic Central Indo-Pacific Eastern Indo-Pacific Lacustrine AS Aquatic Estuarine Setting Marine Water Column Layer Oligohaline Water Mesohaline Water ASCII,netCDF,Best Copy Data Sets; WC Water The Global Temperature Lower Polyhaline Water update at least once a month; Geoform Salinity Regime and Salinity Profile Upper Polyhaline Water 1990-Present; Programme (GTSPP) Euhaline Water global Hyperhaline Water

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CMECS Setting/Comp Class Subclass Datasets Datasets description onent Frozen/Superchilled Water Very Cold Water Cold Water netCDF (netCDF-4 classic),PNG ; Group for High Cool Water update twice a day; Resolution SST Temperature Regime Moderate Water 1981-Present ; (GHRSST) AVHRR Warm Water resolution:4km; Pathfinder Satellite Data Very Warm Water global Hot Water Very Hot Water generated by NCEI, Global Ocean Currents sufficient quality control , current Database (GOCD) spans 1962 to 2013 NetCDF) format F291, netCDF format contains , wave period and Hydroform Class NOAA Marine wave spectrum data, wave Environmental Buoy originate from National Data Buoy Database Center (NDBC) real-time data(Last updated July 16, 2019) Front, Water

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CMECS Setting/Comp Class Subclass Datasets Datasets description onent nutrition WOD native ASCII format、CSV、 Biogeochemical World Ocean chlorophyll netCDF; Feature Dataset(WOD) oxygen .etc update per 3-5 years; Tectonic Setting Physiographic Setting amalgamated from two databases: Beach World Vector Shorelines (WVS) and CIA Beach Berm GSHHG(Global Self- World Data Bank II (WDBII) Boulder Field consistent, Hierarchical, Shapefiles (polygons,lines) ,Native Bank High-resolution binary files; Shore Geography Database) Uncertain update interval ; Shelf five resolutions: crude(c), low(l), GC Geoform intermediate(i), high(h), and full(f) Component Geoform NOAA Global Shallow/Mesophotic Coral Vector (polygon; .shp),KML,WMS Distribution of Coral Reef 1954-2009,global ; Reefs NOAA’s Deep Sea Coral Research and point data with species and depth .etc Deep/Cold-Water Coral Technology Program information of coral reef ; Reef (DSCRTP) CoRIS: Coral provided format : html, csv, json, kml ; Reef Information System .etc Geologic Substrate dbSEABED

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CMECS Setting/Comp Class Subclass Datasets Datasets description onent Biogenic Substrate tables which can be imported into SC Substrate practically any GIS, Anthropogenic Component Continuous updating Substrate Point-data based WOD native ASCII format、CSV、 WOD Ocean Station Zooplankton, netCDF; Data(OSD) Plankton Floating/Suspended 1800,1900-2017; Plants and Macroalgae, globally distributed plankton abundance, Planktonic Biota Phytoplankton, COPEPOD’s global biomass and composition data ; Floating/Suspended plankton database Full databaseare released roughly every Microbes. component few years new data content added each month. NOAA’s Deep Sea Coral BC Biotic Research and point data with species and depth .etc Component Reef Biota Technology Program information of coral reef ; (DSCRTP) CoRIS: Coral provided format : html, csv, json, kml ; Reef Information System Benthic/Attached Biota UNEP WCMC Ocean+ 1:1000000;1934-2015;Vector (polygon, Aquatic Vegetation Bed seagrass point; .shp),Uncertain update interval Global Distribution of 1999-2003 , global , 30m Mangroves USGS; Forested Wetland World Atlas of 1997-2017 , global , 1:1000000 Mangroves

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Table 7 A brief list for available datasets reviewed for mapping global ocean ecosystem

Organizatio Metada Time Resolution/ Class Dataset Website Format Version Update Extent n ta span scale Global Version Vector not Distribution of http://data.unep- UNEP- 1.3 1997- TRUE (polygon; .shp being 30 m global Mangroves wcmc.org/datasets/4 WCMC (June 2000 ) updated USGS 2015) Version not Vector Mangrove World Atlas of http://data.unep- UNEP- 3.0 being 1999- TRUE (polygon; .shp 1:1,000,000 global s Mangroves wcmc.org/datasets/5 WCMC (June updated 2003 ),KML,WMS 2018) . updated Global http://www.eorc.jaxa.jp/ALO Vector UNEP- Version on a 1997- 0.8 arc Mangrove S/en/kyoto/mangrovewatch. TRUE (polygon; .shp global WCMC 2.0 yearly 2017 seconds Watch htm ),WMS basis updated in Vector Version Global intervals Seagrasse http://data.unep- UNEP- (polygon,point 6.0 1934- Distribution of TRUE that are 1:1,000,000 global s wcmc.org/datasets/7 WCMC ; .shp),KML,W (June 2015 Seagrasses uneven MS 2018) in duration

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Organizatio Metada Time Resolution/ Class Dataset Website Format Version Update Extent n ta span scale Correcti Version ons are Global Vector Coral http://data.unep- UNEP- 3.0 made 1954- Distribution of TRUE (polygon; .shp Variable global Reefs wcmc.org/datasets/1 WCMC (June on an 2009 Coral Reefs ),KML,WMS 2018) ad-hoc basis Data are updated Global Vector Version in Distribution of http://data.unep- UNEP- (polygon,point 5.0 1915- Coral TRUE intervals Variable global Cold-water wcmc.org/datasets/3 WCMC ; .shp) , (June 2014 that are Corals KML,WMS 2018) uneven in duration https://www.nodc.noaa.gov/c WOD native Updatin WOD OSD gi- ASCII 1963- Plankton NOAA TRUE WOD18 g with global dataset bin/OC5/SELECT/dbextract. format,CSV,n 1998 WOD pl etCDF AquaMaps 45 million Sealife https://www.aquamaps.org/ observations of nearly 120

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Organizatio Metada Time Resolution/ Class Dataset Website Format Version Update Extent n ta span scale 000 marine species GSHHG(Glob five al Self- version resolutions: consistent, Shapefiles 2.3.7 crude(c), Hierarchical, https://www.ngdc.noaa.gov/ (polygons,line being Unkno NOAA NCEI FALSE (June low(l), global High- mgg/shorelines/gshhs.html s) ,Native updated wn 15, intermediate( resolution binary files. 2017) i), high(h), Geography and full(f) Database) Shoreline NOAA Regiona Shapefiles Average Medium https://shoreline.noaa.gov/d l:Contin NOAA FALSE (polygons,line scale of Resolution ata/datasheets/medres.html ental s) 1:70,000 Shoreline U.S. ESRI Global . Prototype https://dnc.nga.mil/Prototype shapefiles.(se 1:75,000 and except Global NGA \ GSD.php amless smaller the polar Shoreline polyline files) regions netCDF AVHRR (Version: daily 1981- Temperatu NOAA NCEI version Pathfinder https://www.ghrsst.org/ FALSE netCDF-4 update(t Prese 4km Global re GHRSST 5.3 SatelliteData classic) wice) nt PNG

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Organizatio Metada Time Resolution/ Class Dataset Website Format Version Update Extent n ta span scale three a The Global week ; Temperature ASCII ; every 1990- and Salinity https://www.nodc.noaa.gov/ netCDF;Best NOAA NCEI FALSE Sunday Prese Unknown global Profile GTSPP/ Copy Data ; about nt Salinity Programme Sets the 7th (GTSPP) of each month 2000- https://www.nodc.noaa.gov/ The U.S. netCDF,GAD being Argo data FALSE Prese global argo NODC R-3.0 updated nt GEBCO, global gridded spreadsheet, bathymetric shapefile, data sets; the IHO DCDB KML, latest GEBCO grid Bathymetr co-located WMS ,netCDF version: being Unkno Gazetteer of https://www.gebco.net/ FALSE intervals:15 global y with , Esri ASCII GEBCO updated wn Undersea arc-second theNCEI. raster or _2019 Feature GeoTiff Names; the formats GEBCO world map

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Organizatio Metada Time Resolution/ Class Dataset Website Format Version Update Extent n ta span scale Global Relief netCDF, grid https://www.ngdc.noaa.gov/ Unknow Unkno Model, NOAA FALSE georeferenced intervals:1 global mgg/global/global.html n wn ETOPO1 tiff arc-minute dbSEABED,In spatial formation resolution keep Integration https://instaar.colorado.edu/ Point-data Unkno improves as Substrate FALSE updatin global System for ~jenkinsc/dbseabed/ based wn more g Marine datasets are Substrates added

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